2003-10-07 Riverside-San Bernardino-Ontario, CA stagnant mixed-pollution episode
October 7, 2003
Daily PM2.5 peaked at 86.9 µg/m³ near Riverside across
1 covered metro home to 4.7 million people.
Counting the extra PM2.5 above each metro's typical day, this event handed the
average affected resident ≈ 3.2 cigarettes.
Across everyone living in the affected metros, that is the collective equivalent of
≈ 15 million cigarettes.
An awareness illustration of outdoor exposure at 22 µg/m³
per cigarette (Berkeley Earth), counting only the event's ranked days; not a
medical dose.
Why we think this happened
The basis for “Stagnant pollution mixture”
The October 7 Rubidoux peak sits inside a four-day western Inland Empire PM2.5 buildup that appears regional on both surrounding network sampling days. NWS documented an approximately 1,900-foot inversion, stratus moving into the Inland Empire, then exact-date dense fog, a thinning marine layer, and weak onshore flow. Established South Coast source characterization supplies the recurring secondary-plus-combustion mixture. This supports stagnant anthropogenic mixture at possible confidence, while the rotating monitor schedule and missing exact-day speciation prohibit a stronger or source-specific claim.
PossibleThis is a transparent hypothesis supported by limited evidence or an explicit inference, not a definitive attribution.
EPA's certified daily record measured 86.9 micrograms per cubic meter at Rubidoux on October 7. It was the only 24-hour FRM PM2.5 monitor in the metro reporting that date, so the exact-day number cannot by itself establish metro-wide spatial coverage.
National Weather Service San Diego Area Forecast Discussion via Iowa Environmental Mesonet · Oct 6, 2003hypothesis
NWS measured an inversion base near 1,900 feet on October 6 while low clouds moved into the Inland Empire. The exact-date October 7 discussion then reported dense fog, a thinning marine layer, and weak onshore flow. These observations document persistent shallow-layer retention during the rising PM2.5 sequence.
Inference, not direct attribution
rotating_monitor_episode_plus_shallow_inversion_and_basin_profile_possible.v1: This inference is recorded in the catalog methodology.
A cause is more convincing when the record connects three things: something happened,
the air mass moved toward the region, and local instruments responded. Here is how much
of that chain is documented for this event.
rotating_monitor_episode_plus_shallow_inversion_and_basin_profile_possible.v1. This inference is recorded in the catalog methodology.
Inferred
2
Air-mass movement
The transport path has not been reconstructed
The retained record does not yet show how air traveled from the proposed source to
these metros. A trajectory replay or dated plume analysis belongs here.
Research gap
3
Local response
86.9 µg/m³ near Riverside
EPA monitors recorded the event across 1 metro.
The peak daily concentration is roughly 4.0 cigarette-equivalents at the outdoor daily rate.
Before, during, and after the episode: nearby pollutant monitors and surface-weather
stations show what changed. This context tests the “Stagnant pollution mixture” explanation; it does
not assign the cause by itself.
Observed context · not attribution
Riverside-San Bernardino-Ontario, CA
Monitor comparison window 2003-10-04 to 2003-10-10 · PM2.5 target: Rubidoux
6 pollutant signals
Fine-particle pulse86.9 µg/m³
62% above nearby days
Air movement7 kt median wind
1 calm hour observed
What observers saw6 mi minimum visibility
Haze reported during 1 hour
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.586.9 µg/m³
62% higher than surrounding days
Before44 µg/m³ Event86.9 µg/m³ After63.4 µg/m³
PM1030.5 µg/m³
About the same as surrounding days
Before31.5 µg/m³ Event30.5 µg/m³ After41 µg/m³
Carbon monoxide0.734 ppm
11% higher than surrounding days
Before0.627 ppm Event0.734 ppm After0.876 ppm
Nitrogen dioxide27.3 ppb
About the same as surrounding days
Before28.2 ppb Event27.3 ppb After28.5 ppb
Sulfur dioxide0.450 ppb
About the same as surrounding days
Before0.500 ppb Event0.450 ppb After0.390 ppb
Ozone0.041 ppm
About the same as surrounding days
Before0.040 ppm Event0.041 ppm After0.037 ppm
Atmospheric conditions
PALM SPRINGS RGNL, 86 km from the PM2.5 target
Wind7 kt median
12 kt maximum · 1 of 24 observed hours calm
Visibility6 mi minimum
0 observed hours at or below 3 miles
Temperature83.5°F median
72°F to 95°F
Humidity33% median
52% maximum
Source: U.S. EPA AirData daily observations and, where available, nearby ASOS/AWOS
surface observations. Values are descriptive medians over the retained monitor set;
missing measurements remain missing. Transport and source evidence remain separate
layers because this instrument pattern does not assign a cause by itself.
Measured daily PM2.5 at EPA monitors, as cigarette-equivalents
EPA monitors sit in metro areas, so the colour clusters there. Land between and beyond
them is unmeasured, not clean: this map shows where IAQng has readings, not the extent
of the smoke.
—
Episode peak
--cigarettes
The smoke map's scale, replayed over this event: the surface interpolates between
covered metros' daily records, framed to the affected region. Hover for a reading,
click a metro to pin it to the card. Days a monitor did not report draw nothing.
Select a metro on the map to see nearby cameras. Where an operator archive reaches
the event, drag the divider to compare two moments, adjust either date and time, or
play the available event-day frames. Camera imagery is visual context, not an
air-quality measurement or proof of smoke.
No useful public camera views are currently available within 80 km of this metro.
"Cigarettes, whole event" totals a metro's ranked event days at 22 µg/m³ per
cigarette: what a person outdoors there breathed across the event, as the
illustration. "All-time standing" is where this episode's days sit in each metro's
ranked record (worst-area measure, since 1999). Full local context is on each
metro's Air Records page.
Public evidence library
What supports this account
Each card states what a source supports—and what it does not. Official records, research, reporting, community observations, and transparent inferences remain visibly different kinds of evidence.
5 retained sources
Official record
Area Forecast Discussion: dense-fog advisory expired October 7
National Weather Service San Diego via Iowa Environmental Mesonet
NWS San Diego expired a dense-fog advisory on the event morning and reported a thinning marine layer and weak onshore flow; it did not identify a PM2.5 cause.
What it supports
Context for the event; this item does not establish the attributed cause by itself.
Limit
Dense fog and a marine layer are context only; this discussion does not explicitly document a trapping inversion or emitting source.
Official record
Marine inversion and Inland Empire stratus during the October 2003 episode
National Weather Service San Diego Area Forecast Discussion via Iowa Environmental Mesonet
NWS measured an inversion base near 1,900 feet on October 6 while low clouds moved into the Inland Empire. The exact-date October 7 discussion then reported dense fog, a thinning marine layer, and weak onshore flow. These observations document persistent shallow-layer retention during the rising PM2.5 sequence.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
The sounding was taken at San Diego and does not measure the Rubidoux mixing height directly.
Official record
Western Inland Empire PM2.5 episode reconstruction, October 6–9, 2003
U.S. EPA AirData
The surrounding certified samples show that October 7 sat inside a coherent western Inland Empire episode rather than standing alone. On October 6, Rubidoux, San Bernardino, and Ontario measured 77.4, 73.9, and 66.9 micrograms per cubic meter. On October 9, Rubidoux, Riverside-Magnolia, Ontario, Fontana, and San Bernardino measured 76.6, 73.3, 68.9, 64.3, and 62.5, while desert and mountain sites remained 17 or lower. Rubidoux itself stayed above 76 from October 6 through 9.
What it supports
Context for the event; this item does not establish the attributed cause by itself.
Limit
These adjacent-day network samples reconstruct the episode around a rotating FRM schedule; they are not measurements from every site on October 7.
Official record
Rubidoux PM2.5 peak, October 7, 2003
U.S. EPA AirData
EPA's certified daily record measured 86.9 micrograms per cubic meter at Rubidoux on October 7. It was the only 24-hour FRM PM2.5 monitor in the metro reporting that date, so the exact-day number cannot by itself establish metro-wide spatial coverage.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
One reporting monitor cannot establish the exact-day regional footprint.
Scientific research
Characterization of PM2.5 and PM10 in the South Coast Air Basin: spatial variations
Kim et al., Journal of the Air & Waste Management Association
A South Coast AQMD-led characterization found that ammonium, nitrate, sulfate, organic carbon, and elemental carbon dominated basin PM2.5, with especially high inland concentrations at Rubidoux. It establishes the recurring secondary-plus-combustion mixture available to accumulate under the observed shallow-layer conditions.
What it supports
Context for the event; this item does not establish the attributed cause by itself.
Limit
The study is recurring basin context, not an October 7, 2003 chemical sample.
What remains uncertain
No exact-date chemical-speciation or receptor-model allocation was recovered.
Only Rubidoux supplied a 24-hour FRM PM2.5 value on October 7; the broader footprint is reconstructed from October 6 and 9 network samples.
The classification names a broad accumulated mixture, not a unique emitter.
Status and provenance
PossibleThis is a transparent hypothesis supported by limited evidence or an explicit inference, not a definitive attribution.
This episode was grouped from the monitor record by the catalog pipeline and given
its cause from the evidence listed above. It has not been individually reviewed and
signed off, so its boundaries, cause, and name may change as evidence accumulates.
Grouping policy common_sense_root_cause_grouping.v2. The cause label reflects the
assembled evidence above, not an IAQng detection formula. If it is wrong,
tell us.